JPH0367309B2 - - Google Patents

Info

Publication number
JPH0367309B2
JPH0367309B2 JP57219165A JP21916582A JPH0367309B2 JP H0367309 B2 JPH0367309 B2 JP H0367309B2 JP 57219165 A JP57219165 A JP 57219165A JP 21916582 A JP21916582 A JP 21916582A JP H0367309 B2 JPH0367309 B2 JP H0367309B2
Authority
JP
Japan
Prior art keywords
bromine
storage tank
anolyte
catholyte
removal device
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Lifetime
Application number
JP57219165A
Other languages
Japanese (ja)
Other versions
JPS59111279A (en
Inventor
Takashi Hashimoto
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Meidensha Electric Manufacturing Co Ltd
Original Assignee
Meidensha Electric Manufacturing Co Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Meidensha Electric Manufacturing Co Ltd filed Critical Meidensha Electric Manufacturing Co Ltd
Priority to JP57219165A priority Critical patent/JPS59111279A/en
Publication of JPS59111279A publication Critical patent/JPS59111279A/en
Publication of JPH0367309B2 publication Critical patent/JPH0367309B2/ja
Granted legal-status Critical Current

Links

Classifications

    • HELECTRICITY
    • H01ELECTRIC ELEMENTS
    • H01MPROCESSES OR MEANS, e.g. BATTERIES, FOR THE DIRECT CONVERSION OF CHEMICAL ENERGY INTO ELECTRICAL ENERGY
    • H01M10/00Secondary cells; Manufacture thereof
    • H01M10/36Accumulators not provided for in groups H01M10/05-H01M10/34
    • H01M10/365Zinc-halogen accumulators
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E60/00Enabling technologies; Technologies with a potential or indirect contribution to GHG emissions mitigation
    • Y02E60/10Energy storage using batteries

Landscapes

  • Engineering & Computer Science (AREA)
  • Manufacturing & Machinery (AREA)
  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Electrochemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Secondary Cells (AREA)
  • Hybrid Cells (AREA)

Description

【発明の詳細な説明】 本発明は亜鉛臭素電池に係り、詳しくは臭素除
去装置と単電池本体とより構成された液循環型の
亜鉛臭素二次電池に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a zinc bromine battery, and more particularly to a liquid circulation type zinc bromine secondary battery comprising a bromine removal device and a cell main body.

亜鉛−臭素電池はエネルギー密度が高い観点か
ら近年この実用化が研究されている。例えば第1
図は電解液循環型の亜鉛−臭素二次電池の基本的
構成を示すもので、図中1は単電池2は陽極室3
は陰極室、4は隔膜(セパレータ)5は陽極、6
は陰極、7は陽極液、8は陰極液、9は陽極液貯
槽、10は陰極液貯槽、11および12はポンプ
である。これら亜鉛−臭素電池においては、従来
から電流効率(放電々気量/充電々気量×100%)
の向上が望まれていた。
Zinc-bromine batteries have been studied for practical use in recent years because of their high energy density. For example, the first
The figure shows the basic configuration of an electrolyte circulation type zinc-bromine secondary battery.
is a cathode chamber, 4 is a diaphragm (separator), 5 is an anode, 6
is a cathode, 7 is an anolyte, 8 is a catholyte, 9 is an anolyte storage tank, 10 is a catholyte storage tank, and 11 and 12 are pumps. Conventionally, in these zinc-bromine batteries, the current efficiency (discharged capacity/charged capacity x 100%)
It was hoped that improvements would be made.

一般に亜鉛−臭素電池の電圧効率(放電々圧/
充電々圧×100%)を向上せしめるためには、陽
陰極5,6間の距離を短かくし、電圧損失を小さ
くするか、又は使用する電解液中に電導度を向上
せしめる添加剤(支持電解液)を添加すること等
の手段により電圧効率は通常問題とならない程高
効率を維持しうる。然しながら亜鉛−臭素電池の
エネルギー効率は上述の電流効率と電圧効率との
積で表わされる為にいくら電圧効率が高くても、
電流効率が低いと結局エネルギー効率は悪くなつ
てしまうので亜鉛−臭素電池における低い電流効
率の向上が従来からの課題であつた。
In general, the voltage efficiency (discharge voltage/
In order to improve the charge voltage x 100%, the distance between the anode and cathode 5 and 6 must be shortened to reduce voltage loss, or the electrolyte used must contain an additive (supporting electrolyte) that improves conductivity. The voltage efficiency can be maintained at such a high efficiency that it does not normally pose a problem by adding a liquid or the like. However, the energy efficiency of a zinc-bromine battery is expressed as the product of the above-mentioned current efficiency and voltage efficiency, so no matter how high the voltage efficiency is,
If the current efficiency is low, the energy efficiency will eventually deteriorate, so improving the low current efficiency of zinc-bromine batteries has been a conventional problem.

従来亜鉛−臭素電池の電流効率の向上に関する
因子としては、隔膜、電極、電解液の組成、隔膜
−電極間の距離、電流密度、充電深度等が考えら
れている。先ず隔膜の作用は、充電時発生する陽
極室の臭素を対極の陰極室に拡散させない機能を
有し隔膜としてイオン交換膜、多孔質膜が使用さ
れている。イオン交換膜は臭素などの陽極で発生
した臭素(Br2)の拡散をかなり抑制し、陰極上
の析出亜鉛との自己放電をおさえるため、電池性
能として高い90〜99%の電流効率を与えるが、し
かし電解液中での膜電気抵抗が高いため電圧効率
を低下させる。これに対して多孔質膜はイオン交
換膜に比べて膜電気抵抗が小さく電圧効率の低下
は少ないが前述の臭素(Br2)拡散はイオン交換
膜程おさえることが出来ず、電流効率としては70
〜85%程度である。
Factors related to improving the current efficiency of conventional zinc-bromine batteries include the composition of the diaphragm, electrodes, and electrolyte, the distance between the diaphragm and the electrode, current density, charging depth, and the like. First, the function of the diaphragm is to prevent bromine generated in the anode chamber during charging from diffusing into the cathode chamber of the counter electrode, and an ion exchange membrane or a porous membrane is used as the diaphragm. The ion exchange membrane considerably suppresses the diffusion of bromine (Br 2 ) generated at the anode, and suppresses self-discharge with the zinc deposited on the cathode, giving the battery a high current efficiency of 90 to 99%. However, the high membrane electrical resistance in the electrolyte reduces voltage efficiency. On the other hand, porous membranes have a lower membrane electrical resistance than ion exchange membranes and less decrease in voltage efficiency, but cannot suppress the aforementioned bromine (Br 2 ) diffusion as well as ion exchange membranes, and current efficiency is 70%.
~85%.

またこの自己拡散を少なくし、電流効率を向上
させるために隔膜の厚みを厚くする方法が採用さ
れる場合があるが、これは逆に膜抵抗(例えば電
気抵抗および亜鉛イオンの透過抵抗)を増加し電
圧効率を低下せしめる欠点を有するので好ましく
ない。
In addition, in order to reduce this self-diffusion and improve current efficiency, a method of increasing the thickness of the diaphragm is sometimes adopted, but this conversely increases membrane resistance (for example, electrical resistance and permeation resistance of zinc ions). However, it is not preferred because it has the disadvantage of lowering voltage efficiency.

また電極としては、特に陽極側での放電々位の
高いもの程電流効率も良くなるので、放電々位向
上の為に電極に特殊な工夫をこらす必要があり経
済上有利ではない。
Further, as for electrodes, the higher the discharge level, especially on the anode side, the better the current efficiency, so it is necessary to make special arrangements for the electrode in order to improve the discharge level, which is not economically advantageous.

電解液の組成としては種々の添加剤による組成
の提案があり、夫々或る程度効果をあげているが
種々の条件によつて、その組成も変化し未だ本問
題を完全に解決されていない。
Various additives have been proposed for the composition of the electrolytic solution, and although each has been effective to some extent, the composition changes depending on various conditions, and this problem has not yet been completely solved.

以上述べた以外の隔膜−電極間の距離、電流密
度、充電深度等の因子は、電流効率の向上のみで
決定される訳ではなく、それ以上に亜鉛−臭素電
池全体のエネルギー密度の点からも検討される内
容であり一般的に電流効率の向上のためばかりで
簡単に決定されない因子である。この様に亜鉛−
臭素電池の電流効率向上対策としては他の方法で
改善する必要が従来から望まれていた。
Factors other than those mentioned above, such as the distance between the diaphragm and the electrode, current density, and depth of charge, are determined not only by improving current efficiency, but also from the viewpoint of the overall energy density of the zinc-bromine battery. This is a matter of consideration, and is generally a factor that is not easily determined because it is only for improving current efficiency. In this way, zinc-
It has long been desired that other methods be used to improve the current efficiency of bromine batteries.

本発明者は先に陽極上に発生する臭素の陰極室
への拡散による電流効率低下を防止するために、
比較的に電圧効率の高い多孔質膜を隔膜として用
いた亜鉛−臭素二次電池において、陰極室内の陰
極液圧と陽極室内の陽極液圧とを変動せしめた場
合のイオン交換膜に比べ透過性の大きい多孔質膜
を通過する電解液移動量と電流効率との関係を実
験研究した結果、その間に大きな有意差があるこ
とを見出した。即ち陽極室と陰極室とを隔膜とし
て特に多孔質膜により分離し、陽極室内の陽極液
および陰極室内の陰極液を循環せしめる亜鉛−臭
素二次電池において、陰極室内の陰極液圧を陽極
室内の陽極液圧より大とし、陰極液を多孔質膜を
通して陽極室内に移動せしめ、陽極上に発生した
臭素を隔膜を通して、陰極上に拡散し、陰極上の
亜鉛と自己放電することを防止する発明を行なつ
た。添付第2図は上記発明の実施態様図である。
また陰極液を移動せしめる手段としては、第2図
に示す如く循環系路の配管抵抗損失に差を生ぜし
めるか夫々の循環ポンプ11および12の出力に
差をつけ循環量を変える方法を提案し、これによ
り、電流効率が液移動の行なわれない場合に比し
著しく向上することを実験的に明らかにした。然
しながら本法は充放電サイクル運転中に増加した
陽極液貯槽9中の陽極液7特に充電初期または放
電末期における臭素含有量の少い陽極液7または
陽極液の上澄液を陰極液貯槽10に充放電中また
は充放電後の停止中に陽極液貯槽9と陰極液貯槽
10とを結ぶ共通配管のバルブ18を経由し戻す
必要があり結局陽極液中の臭素が陰極液中に移動
する問題がある。
In order to prevent the current efficiency from decreasing due to the diffusion of bromine generated on the anode into the cathode chamber,
In a zinc-bromine secondary battery using a porous membrane with relatively high voltage efficiency as a diaphragm, the permeability is lower than that of an ion exchange membrane when the catholyte pressure in the cathode chamber and the anolyte liquid pressure in the anode chamber are varied. As a result of an experimental study on the relationship between the amount of electrolyte transfer through a large porous membrane and current efficiency, it was found that there was a large significant difference between them. In other words, in a zinc-bromine secondary battery in which the anode chamber and the cathode chamber are separated by a particularly porous membrane as a diaphragm, and the anolyte in the anode chamber and the catholyte in the cathode chamber are circulated, the catholyte pressure in the cathode chamber is controlled by the pressure in the anode chamber. The present invention is to increase the pressure of the anolyte to be higher than that of the anolyte, move the catholyte into the anode chamber through a porous membrane, diffuse bromine generated on the anode through the diaphragm onto the cathode, and prevent self-discharge with zinc on the cathode. I did it. Attached FIG. 2 is a diagram showing an embodiment of the above invention.
In addition, as a means for moving the catholyte, we have proposed a method of varying the amount of circulation by creating a difference in piping resistance loss in the circulation path or by differentiating the output of each circulation pump 11 and 12, as shown in Figure 2. It has been experimentally demonstrated that this significantly improves current efficiency compared to the case without liquid movement. However, in this method, the anolyte 7 in the anolyte storage tank 9 that has increased during charge/discharge cycle operation, especially the anolyte 7 with a low bromine content at the beginning of charge or the end of discharge, or the supernatant liquid of the anolyte is transferred to the catholyte storage tank 10. During charging and discharging or when stopped after charging and discharging, it is necessary to return the anolyte through the valve 18 of the common pipe connecting the anolyte storage tank 9 and the catholyte storage tank 10, resulting in the problem that bromine in the anolyte moves into the catholyte. be.

本発明の目的は亜鉛−臭素電池の電流効率を更
に改良向上安定せしめるにある。
The object of the present invention is to further improve and stabilize the current efficiency of zinc-bromine batteries.

本発明の要旨は陽極室と陰極室とを隔膜特に多
孔質膜により分離し、陽極室内の陽極液および陰
極室内の陰極液を夫々陽極液貯槽および陰極液貯
槽を経由し循環せしめ、陰極室内の陰極液圧を陽
極室内の陽極液圧より大にし、陰極液を多孔質膜
を通して陽極室内に移動せしめるように構成した
亜鉛−臭素電池において、陽極液貯槽と陰極液貯
槽間に臭素除去装置を設け、陽極室内に移動した
電解液を臭素除去装置に導入し、電解液中の臭素
濃度を低下せしめ脱臭素電解液を陰極液貯槽に戻
し、陰極上の亜鉛と自己放電をすることを防止す
ることにより、電流効率を向上せしめた亜鉛−臭
素二次電池を提供するにある。
The gist of the present invention is to separate an anode chamber and a cathode chamber by a diaphragm, particularly a porous membrane, circulate the anolyte in the anode chamber and the catholyte in the cathode chamber through an anolyte storage tank and a catholyte storage tank, respectively, and In a zinc-bromine battery configured such that the catholyte pressure is greater than the anolyte pressure in the anode chamber and the catholyte is moved into the anode chamber through a porous membrane, a bromine removal device is provided between the anolyte storage tank and the catholyte storage tank. The electrolyte that has moved into the anode chamber is introduced into the bromine removal device to reduce the bromine concentration in the electrolyte, and the debrominated electrolyte is returned to the catholyte storage tank to prevent self-discharge with zinc on the cathode. Accordingly, it is an object of the present invention to provide a zinc-bromine secondary battery with improved current efficiency.

更に本発明は臭素濃度を低下せしめる臭素除去
装置として、 (1) 亜鉛−臭素電解槽を形成せしめたことを特徴
とする (2) ポンプならびに隔膜として多孔質膜、スルフ
オン化等によりイオン交換性を持たせた多孔質
膜ならびにイオン交換膜を用い電解液を過す
る構造を特徴とする (3) 臭素を錯化せしめる添加剤の液中を通し臭素
錯化物を合成せしめる低臭素濃度電解液を得る
ことを特徴とする。
Furthermore, the present invention is a bromine removal device for reducing bromine concentration, characterized in that (1) a zinc-bromine electrolytic cell is formed; (2) a porous membrane, sulfonation, etc. are used as a pump and a diaphragm to improve ion exchange properties; It is characterized by a structure in which the electrolyte is passed through using a porous membrane and an ion exchange membrane.(3) Obtaining a low bromine concentration electrolyte that allows the synthesis of bromine complexes by passing the additive that complexes bromine through the solution. It is characterized by

等を用いる亜鉛−臭素電池である。This is a zinc-bromine battery using

以下添付図面に基いて更に本発明の詳細につい
て述べる。
The present invention will be further described in detail below based on the accompanying drawings.

第3図乃至第8図は臭素除去装置を備えた亜鉛
−臭素電池の実施態様を示す模式図である。
3 to 8 are schematic diagrams showing embodiments of a zinc-bromine battery equipped with a bromine removal device.

第3図は、亜鉛−臭素電解構造を特徴とした臭
素除去装置を説明するための模式図であり第4図
は第3図に示す臭素除去装置を備えた本発明の一
実施例を示す亜鉛−臭素二次電池の基本的構成を
示す模式図。
FIG. 3 is a schematic diagram for explaining a bromine removal device featuring a zinc-bromine electrolytic structure, and FIG. - Schematic diagram showing the basic configuration of a bromine secondary battery.

第5図は多孔質膜等の隔膜を用い臭素濃度の低
い電解液を得ることを特徴とした臭素除去装置を
備えた亜鉛−臭素二次電池の基本的構成を示す模
式図。第6図は第5図に示す態様と異なる臭素除
去装置を示す模式図。第7図は臭素を錯化せしめ
る添加剤溶液中を電解液が通過することにより臭
素錯化物として臭素を除去することを特徴とする
臭素除去装置を備えた亜鉛−臭素二次電池の基本
的構成を示す模式図であり第8図は第7図に示す
臭素除去装置の他の実施態様図である。
FIG. 5 is a schematic diagram showing the basic configuration of a zinc-bromine secondary battery equipped with a bromine removal device characterized by using a diaphragm such as a porous membrane to obtain an electrolytic solution with a low bromine concentration. FIG. 6 is a schematic diagram showing a bromine removal apparatus different from the embodiment shown in FIG. 5. Figure 7 shows the basic configuration of a zinc-bromine secondary battery equipped with a bromine removal device that removes bromine as a bromine complex by passing an electrolytic solution through an additive solution that complexes bromine. FIG. 8 is a diagram showing another embodiment of the bromine removal apparatus shown in FIG. 7.

以上の図面中同一符号は同じ機能を示すもので
ある。
The same reference numerals in the above drawings indicate the same functions.

第2図において単電池1内部の陽極室2と陰極
室3との間に圧力差を生じさせ特に多孔質膜より
なる隔膜4を通して、陰極室内の圧力が陽極室内
より大なる場合陰極室3より陰極液8が陽極室2
に移動するため、陽極液7中における臭素
(Br2)の陰極室3中への拡散を抑制し、自己放
電をおさえ、電流効率が、圧力差を付加しない状
態に比して著しく向上せしめうるものである。
In Fig. 2, a pressure difference is created between the anode chamber 2 and the cathode chamber 3 inside the unit cell 1, and when the pressure inside the cathode chamber is higher than that of the anode chamber, the pressure inside the cathode chamber 3 is increased through the diaphragm 4 made of a porous membrane. The catholyte 8 is in the anode chamber 2
Therefore, the diffusion of bromine (Br 2 ) in the anolyte 7 into the cathode chamber 3 is suppressed, self-discharge is suppressed, and the current efficiency can be significantly improved compared to a state where no pressure difference is applied. It is something.

陰極液の移動を生ぜしめるための圧力差は第1
には陰極液8の循環系路(陰極室3→出口配管1
4→陰極液貯槽10→人口配管16→ポンプ12
→陰極室3)の出口配管14から入口配管16ま
での配管抵抗損失を陽極液7の循環系路(陽極室
2→出口配管13→陽極液貯槽9→入口配管15
→ポンプ11→陽極室2)の出口配管13から入
口配管15までの配管抵抗損失より大きくする方
法であり、具体的には配管14,16の、断面積
または長さを配管13,15の断面積または長さ
をより小さくしたり長くする方法、或は陰極室出
口配管14に、弁17を設け陰極室内の液圧を上
昇せしめる。
The pressure difference that causes the movement of the catholyte is the first
is the catholyte 8 circulation system (cathode chamber 3 → outlet piping 1
4 → catholyte storage tank 10 → artificial piping 16 → pump 12
→The piping resistance loss from the outlet piping 14 to the inlet piping 16 of the cathode chamber 3) is calculated from the circulation system path of the anolyte 7 (anode chamber 2 → outlet piping 13 → anolyte storage tank 9 → inlet piping 15)
→ Pump 11 → Anode chamber 2) This is a method of making the pipe resistance loss larger than the pipe resistance loss from the outlet pipe 13 to the inlet pipe 15. Specifically, the cross-sectional area or length of the pipes 14 and 16 is The area or length may be made smaller or longer, or a valve 17 may be provided in the cathode chamber outlet piping 14 to increase the liquid pressure within the cathode chamber.

次に、第2としては陰極液8の循環量を陽極液
7の循環量より大とする方法であり、そのために
は陰極液用ポンプ12の出力を陽極液用ポンプ1
1の出力より大とする。
Next, the second method is to make the circulation amount of the catholyte 8 larger than the circulation amount of the anolyte 7, and for that purpose, the output of the catholyte pump 12 is increased from the output of the anolyte pump 12.
1 output.

以上の如く陰極室3内の陰極液8を圧加するこ
とにより陰極液を陽極室2内に移動せしめ亜鉛−
臭素電池の充放電を行なう場合陽極液貯槽9中の
陽極液7は移動電解液のため増加し続ける。増加
した液を特に充電初期または放電末期における臭
素含有量の少い状態の陽極液あるいは陽極液の上
澄液として陽極液貯槽と陰極液貯槽間の共通配管
中のバルブ18により徐々に陰極液貯槽10に戻
すかまたは、放電の後に一般に“洗い”と云われ
る完全放電の時にバルブ18を開くことにより陰
極液貯槽10に共通配管を経由して電解液を戻
す。この場合前者の戻し方法が後者の戻し方法に
比して電流効率の増加は少ない。この陰陽極液の
圧力差により電解液を陽極側に移動することによ
り電流効率を増加せしめる方法においては、充放
電中または充放電後において電解液を陰極側に戻
す必要があり、結局陽極液中の臭素が陰極液中に
移動することならびに運転を中断する問題等が生
ずる。
As described above, by pressurizing the catholyte 8 in the cathode chamber 3, the catholyte is moved into the anode chamber 2.
When charging and discharging a bromine battery, the anolyte 7 in the anolyte storage tank 9 continues to increase because it is a mobile electrolyte. The increased liquid is gradually transferred to the catholyte storage tank using the valve 18 in the common piping between the anolyte storage tank and the catholyte storage tank, as an anolyte with a low bromine content or a supernatant liquid of the anolyte, especially at the beginning of charging or at the end of discharge. The electrolyte is returned to the catholyte reservoir 10 via the common piping by opening the valve 18 at full discharge, commonly referred to as a "wash", after the discharge. In this case, the former return method causes a smaller increase in current efficiency than the latter return method. In this method of increasing current efficiency by moving the electrolyte to the anode side using the pressure difference between the catholyte and the anolyte, it is necessary to return the electrolyte to the cathode side during or after charging and discharging, and eventually the electrolyte is transferred to the anode side. bromine migrates into the catholyte, causing problems such as interruption of operation.

従つて本発明者は陽極液貯槽9と陰極液貯槽1
0間に臭素除去装置を設け、本除去装置と亜鉛−
臭素電池とを循環導管によつて導通せしめた亜鉛
−臭素二次電池を発明するに至つたものである。
Therefore, the inventor has developed an anolyte storage tank 9 and a catholyte storage tank 1.
A bromine removal device is installed between 0 and 0, and this removal device and zinc
This led to the invention of a zinc-bromine secondary battery that is connected to a bromine battery through a circulation conduit.

第3図及び第4図は陽極液側即ち陽極液貯槽9
に移動した電解液7を陰極液側即ち陰極液貯槽1
0に戻すに当りその中間に臭素除去装置21を設
けた例である。臭素除去装置21は陽極25、陰
極26を有し陽極室22と陰極室23は多孔質膜
よりなる隔膜24にて分離された亜鉛−臭素電解
構造を特徴とする装置である。亜鉛−臭素電池1
と異なる点は、陰極室23の陰極液8は導管36
によつて陽極液貯槽9と接続され、他方の導管3
4によつて陰極液貯槽10と連通されていること
である。19は充放電器、39は臭素除去装置用
の補助電源装置、46は電池の陽極5と臭素除去
装置の陰極25との絶縁支持部である。
Figures 3 and 4 show the anolyte side, that is, the anolyte storage tank 9.
The electrolyte 7 transferred to the catholyte side, that is, the catholyte storage tank 1
This is an example in which a bromine removal device 21 is provided in the middle when returning to zero. The bromine removal apparatus 21 is an apparatus characterized by a zinc-bromine electrolytic structure having an anode 25 and a cathode 26, and an anode chamber 22 and a cathode chamber 23 separated by a diaphragm 24 made of a porous membrane. Zinc-bromine battery 1
The difference is that the catholyte 8 in the cathode chamber 23 is connected to the conduit 36.
is connected to the anolyte reservoir 9 by the other conduit 3
4 communicates with the catholyte storage tank 10. 19 is a charger/discharger, 39 is an auxiliary power supply device for the bromine removal device, and 46 is an insulating support portion between the anode 5 of the battery and the cathode 25 of the bromine removal device.

斯る構成の装置において電池1の充放電運転前
に補助電源39(特に電池本体放電後の完全放電
即ち洗い時の電池を電源とすると良い)により臭
素除去装置に電流を流し陰極26上に亜鉛を電着
させる。一方陽極25上で発生した臭素分子は導
管33,35を通して陽極液貯槽9に拡散せしめ
る。このように臭素除去装置21の陰極26上に
亜鉛を電着させた後電池1を陰陽両極液の圧力差
をポンプ11とポンプ12の出力差により電解液
を陽極側に移動する方法に2充放電器19を用い
運転すると電池1内の陰極室3から隔膜4を通し
て陽極室2に移動した電解液は導管13を経由し
て陽極液貯槽9に導入されその水位が上がり陰極
液貯槽10の水位との間に差を生ずる。その水位
差によつて陽極液7が導管36を経由して臭素除
去装置21の陰極室23に流れ込む。次に流れ込
んだ陽極液7中の臭素と陰極26上の析出亜鉛と
が自己放電を起し、陰極室23を通過後は臭素濃
度の低い電解液となり導管34を通つて陰極液貯
槽10に導入される。即ち電池1の運転により陽
極側に移動した電解液を陰極側に戻す場合臭素除
去装置21によつて臭素濃度の低い電解液を戻し
うることとなり、電流効率の良い運転を可能とす
る。
In a device having such a configuration, before charging and discharging the battery 1, a current is passed through the bromine removal device by the auxiliary power source 39 (in particular, it is preferable to use the battery during complete discharge, i.e., washing, after the battery main body is discharged) to remove zinc onto the cathode 26. Electrodeposit. On the other hand, bromine molecules generated on the anode 25 are diffused into the anolyte storage tank 9 through conduits 33 and 35. After zinc was electrodeposited on the cathode 26 of the bromine removal device 21 in this way, the battery 1 was charged twice using a method in which the pressure difference between the anode and cathode solutions was used to move the electrolyte to the anode side using the output difference between the pumps 11 and 12. When the discharger 19 is used in operation, the electrolyte that moves from the cathode chamber 3 in the battery 1 to the anode chamber 2 through the diaphragm 4 is introduced into the anolyte storage tank 9 via the conduit 13, and its water level rises to lower the water level in the catholyte storage tank 10. There is a difference between Due to the water level difference, the anolyte 7 flows into the cathode chamber 23 of the bromine removal device 21 via the conduit 36. Next, the bromine in the anolyte 7 that has flowed in and the zinc deposited on the cathode 26 cause self-discharge, and after passing through the cathode chamber 23, it becomes an electrolyte with a low bromine concentration and is introduced into the catholyte storage tank 10 through the conduit 34. be done. That is, when the electrolytic solution that has moved to the anode side due to the operation of the battery 1 is returned to the cathode side, the electrolytic solution with a low bromine concentration can be returned to the cathode side by the bromine removal device 21, thereby enabling operation with high current efficiency.

臭素除去装置21の陰極26上に亜鉛を析出さ
せる補助電源39の代りに、電池1の端子資から
切換スイツチ47によつて臭素除去装置の電源を
取つてもよい。またこの場合これを電池の洗い即
ち完全放電の時に行なえばシステム全体の損失が
少なくなり、効率が向上することとなる。更に第
3図に示す如く臭素除去装置21と電池1を積層
した構造としている場合は設置場所を取らず、装
置の電極面積を大きく取れる利点もある。
Instead of the auxiliary power source 39 for depositing zinc on the cathode 26 of the bromine remover 21, the bromine remover 21 may be powered from the terminals of the battery 1 by means of a changeover switch 47. In this case, if this is done when the battery is washed or completely discharged, the loss of the entire system will be reduced and the efficiency will be improved. Furthermore, if the bromine removal device 21 and the battery 1 are stacked as shown in FIG. 3, there is an advantage that the installation space is not taken up and the electrode area of the device can be increased.

次に第2の臭素除去装置の実施態様を第5図な
らびに第6図に基いて述べる。
Next, an embodiment of the second bromine removal device will be described based on FIGS. 5 and 6.

第5図において亜鉛臭素積層電池1を陽極液貯
槽9ならびに陰極液貯槽10とを導管13および
14にて連通せしめ、陽極液用ポンプ11の出口
側を電池1側と臭素除去装置21に夫々導管15
と導管33に分岐せしめ、導管33中にバルブ2
8を設ける。一方臭素除去装置21は液室31お
よび液室32を隔膜24により分離せしめた構造
とし液室31の他方に導管35を、その導管35
中にバルブ27を介して陽極液貯槽9と連通せし
め、また液室32と陰極液貯槽10との間を導管
34にて連結する構造とする。
In FIG. 5, the zinc-bromine stacked battery 1 is connected to the anolyte storage tank 9 and the catholyte storage tank 10 through conduits 13 and 14, and the outlet side of the anolyte pump 11 is connected to the battery 1 side and the bromine removal device 21 through conduits, respectively. 15
and branched into a conduit 33, and a valve 2 is installed in the conduit 33.
8 will be provided. On the other hand, the bromine removal device 21 has a structure in which a liquid chamber 31 and a liquid chamber 32 are separated by a diaphragm 24, and a conduit 35 is connected to the other side of the liquid chamber 31.
The interior thereof is communicated with the anolyte storage tank 9 through a valve 27, and the liquid chamber 32 and the catholyte storage tank 10 are connected through a conduit 34.

斯る構成の装置において、前述の実施態様例と
同様に電池1の運転により陽極液貯槽9に移動し
た電解液と陰極液貯槽10に戻すに際し、バルブ
27とバルブ28を調節して液室31内の圧力と
流入量を調整しながら隔膜24を通して液室32
に電解液を移動せしめる。この隔膜24は多孔質
膜、イオン交換性を持たせた多孔質膜或はイオン
交換膜等より構成されているので電解液中の臭素
は隔膜により過され液室32には臭素濃度の低
い電解液が導入され、この電解液は導管34によ
り陰極液貯槽10に戻される。この結果電解液中
の臭素濃度を抑制することができ電気の電流効率
を向上せしめる。
In the apparatus having such a configuration, when returning the electrolyte that has moved to the anolyte storage tank 9 due to the operation of the battery 1 to the catholyte storage tank 10, the valves 27 and 28 are adjusted to close the liquid chamber 31. The liquid chamber 32 is passed through the diaphragm 24 while adjusting the pressure and inflow amount inside the liquid chamber 32.
Transfer the electrolyte to Since the diaphragm 24 is composed of a porous membrane, a porous membrane with ion exchange properties, an ion exchange membrane, etc., bromine in the electrolyte is passed through the diaphragm, and the electrolyte with a low bromine concentration is stored in the liquid chamber 32. A liquid is introduced and this electrolyte is returned to the catholyte reservoir 10 by conduit 34. As a result, the bromine concentration in the electrolyte can be suppressed and the electric current efficiency can be improved.

第6図は前述の臭素除去装置21の隔膜を複数
枚とし液室を多く設けた例で、かつバルブ27の
代りに導管35より断面積の小さい導管よりなる
チヤネル37によつてバルブ27の絞り比と同様
な液抵抗をもたせ各液室に導入し臭素濃度の低い
電解液を得る例である。さらに増加した陽極液を
ポンプ11によつて強制的に戻すことなくバルブ
28を閉じ、充放電中に生じた陰陽液面レベル差
によつて増加した陽極液を導管35→チヤネル3
7→隔膜24→導管34の流れで戻すことも出来
る利点がある。本臭素除去装置は構造的に簡単で
かつエネルギーを別に用いないことが利点であ
る。
FIG. 6 shows an example in which the bromine removal device 21 described above has a plurality of diaphragms and a large number of liquid chambers, and instead of the valve 27, the valve 27 is throttled by a channel 37 consisting of a conduit having a smaller cross-sectional area than the conduit 35. This is an example of obtaining an electrolytic solution with a low bromine concentration by introducing it into each liquid chamber with the same liquid resistance as the bromine ratio. Furthermore, the valve 28 is closed without forcibly returning the increased anolyte by the pump 11, and the anolyte increased due to the difference in the level of the positive and negative fluid that occurs during charging and discharging is transferred from the conduit 35 to the channel 3.
There is an advantage that the flow can be returned by the flow of 7 → diaphragm 24 → conduit 34. The advantage of this bromine removal device is that it is structurally simple and does not require additional energy.

次に第3の臭素を錯化せしめる添加剤により臭
素錯化物を合成し低濃度に臭素を除去する装置の
実施態様例を第7図ならびに第8図に基いて述べ
る。
Next, an embodiment of an apparatus for synthesizing a bromine complex using a third bromine complexing additive and removing bromine to a low concentration will be described with reference to FIGS. 7 and 8.

第7図において電池1の陽極室2を導電13,
15によりポンプ11を介して陽極液貯槽9に導
通せしめ同様に陰極室3を導管14,16により
ポンプ12を介して陰極液貯槽10と導通せしめ
る。臭素除去装置21は陽極液貯槽9と導管33
および導管35により、陰極液貯槽10とは導管
34により導通されている。臭素除去装置21内
部には臭素と反応して臭素錯化物を合成する様な
添加剤40例えばアミン化合物(トリプロピルア
ミン臭素酸塩、トリブチルアミン臭素酸塩等)3
級、4級アミン化合物(メチル、エチル、モルホ
リニウム塩、メチル、エチル、ピロリジウム塩、
メチル、デシル、ピロリジウム塩等)を大量に入
れてあり、導管35中の隔膜44により陽極液貯
槽9中の陽極液7と分離せしめている。
In FIG. 7, the anode chamber 2 of the battery 1 is connected to the conductor 13,
15 connects the catholyte chamber 3 to the anolyte storage tank 9 via the pump 11, and similarly connects the cathode chamber 3 to the catholyte storage tank 10 via the pump 12 via conduits 14 and 16. The bromine removal device 21 includes an anolyte storage tank 9 and a conduit 33.
The catholyte storage tank 10 is connected to the catholyte storage tank 10 by a conduit 34 and a conduit 35 . Inside the bromine removal device 21, there is an additive 40 that reacts with bromine to synthesize a bromine complex, such as an amine compound (tripropylamine bromate, tributylamine bromate, etc.) 3.
and quaternary amine compounds (methyl, ethyl, morpholinium salts, methyl, ethyl, pyrrolidium salts,
methyl, decyl, pyrrolidium salts, etc.), and is separated from the anolyte 7 in the anolyte storage tank 9 by a diaphragm 44 in the conduit 35.

次に本臭素除去装置21の作用について述べ
る。前述の実施態様例と同様に電池1の運転によ
り陽極液貯槽9に移動した電解液を陰極液貯槽1
0に戻すに際し、両貯槽の水位差により導管33
を通して陽極液貯槽9内の臭素濃度の高い電解液
が臭素除去装置21内に導入され、前記添加剤と
接触混合した際に電解液中の臭素が添加剤によつ
て臭素錯化合物に変成する。かくして臭素濃度が
低下した電解液は臭素除去装置内部に上澄液とし
て分離し導管34を通つて、陰極液貯槽10に戻
る。臭素と反応して生成された臭素錯化物は添加
剤40中に沈降し導管35の隔膜44の所まで進
む。この隔膜44を通して陽極液貯槽9中の陽極
液7の臭素濃度に対応した速度で陽極液中に滲透
拡散してゆく。この様にして電池1内部で陽極側
に移動した液は本臭素除去装置21により低臭素
濃度の電解液として陰極側に戻り、電解液中の臭
素濃度を抑制し得て、電池の電流効率を向上する
ことが出来る。
Next, the operation of the present bromine removal device 21 will be described. As in the embodiment described above, the electrolyte transferred to the anolyte storage tank 9 due to the operation of the battery 1 is transferred to the catholyte storage tank 1.
When returning to zero, due to the water level difference between the two storage tanks, the conduit 33
The electrolytic solution with a high bromine concentration in the anolyte storage tank 9 is introduced into the bromine removal device 21 through the anolyte storage tank 9, and when mixed with the additive, the bromine in the electrolytic solution is converted into a bromine complex compound by the additive. The electrolyte with the reduced bromine concentration is separated as a supernatant inside the bromine removal device and returned to the catholyte storage tank 10 through conduit 34. The bromine complex formed by reaction with bromine settles into the additive 40 and passes to the diaphragm 44 of the conduit 35. Through this diaphragm 44, bromine permeates and diffuses into the anolyte at a rate corresponding to the bromine concentration of the anolyte 7 in the anolyte storage tank 9. The liquid that has moved to the anode side inside the battery 1 in this way returns to the cathode side as an electrolyte with a low bromine concentration by the present bromine removal device 21, suppressing the bromine concentration in the electrolyte and increasing the current efficiency of the battery. It can be improved.

なお第8図は添加剤の種類によつて生成した臭
素錯化物が沈澱しないで浮遊するものがあるので
臭素除去装置21の添加剤の液上に配管34の下
辺より低い位置に多孔度の大きい膜、布等よりな
る隔膜45を用いた例である。
In addition, FIG. 8 shows that, depending on the type of additive, the generated bromine complex does not precipitate but floats, so a large porosity is placed above the additive liquid in the bromine removal device 21 at a position lower than the lower side of the pipe 34. This is an example using a diaphragm 45 made of a membrane, cloth, or the like.

次に本発明の実施例を臭素除去装置を具備しな
い場合の比較例と共に述べる。
Next, examples of the present invention will be described together with comparative examples in which a bromine removal device is not provided.

(1) 比較例 添付第2図に示す如き電池構成において、隔膜
4として市販の多孔質膜厚み0.4mm(旭化成(株)製
FP膜)のものを用い、電解液として臭化亜鉛溶
液3モル/に錯化剤としてメチル、エチル、モ
ルホリニウム・ブロマイド0.5モル/およびメ
チル、エチル、ピロリジウム ブロマイド0.5モ
ル/計1モル/添加したもの、更に陽極液に
は0.2モル/の臭素を添加した。
(1) Comparative example In the battery configuration shown in the attached Figure 2, a commercially available porous membrane with a thickness of 0.4 mm (manufactured by Asahi Kasei Corporation) was used as the diaphragm 4.
FP membrane) was used, and 0.5 mole of methyl, ethyl, morpholinium bromide as a complexing agent and 0.5 mole of methyl, ethyl, pyrrolidium bromide were added to 3 mole of zinc bromide solution as the electrolyte, and 1 mole of methyl, ethyl, and pyrrolidium bromide as a complexing agent. Furthermore, 0.2 mol/bromine was added to the anolyte.

ポンプ11および12は直流電動機付ポンプを
用い入力電圧、電流を調整して、各電解液の圧力
を調整した。
Pumps 11 and 12 were DC motor pumps, and the input voltage and current were adjusted to adjust the pressure of each electrolytic solution.

また充電は電流密度20mA/cm2で3時間行な
い、放電は電流密度20mA/cm2で電池電圧が1ボ
ルトに低下するまで行なつた。
Charging was carried out for 3 hours at a current density of 20 mA/cm 2 , and discharging was carried out at a current density of 20 mA/cm 2 until the battery voltage decreased to 1 volt.

以上の条件で両電解液のポンプ吐出圧を0.1
Kg/cm2で運転した場合の電流効率は82%であつ
た。
Under the above conditions, the pump discharge pressure of both electrolytes was set to 0.1.
The current efficiency when operated at Kg/cm 2 was 82%.

次に陽極液ポンプ11吐出圧を0.1Kg/cm2陰極
液ポンプ12吐出圧を0.2Kg/cm2とし陽極液に移
動した電解液はバルブ18を開け陰陽極液貯槽を
つなぐことにより戻した。
Next, the discharge pressure of the anolyte pump 11 was set to 0.1 Kg/cm 2 and the discharge pressure of the catholyte pump 12 was set to 0.2 Kg/cm 2 , and the electrolyte that had moved to the anolyte was returned by opening the valve 18 and connecting the catholyte and anolyte storage tanks.

この場合の電流効率は85%であつた。 The current efficiency in this case was 85%.

実施例 1 第3図に示す本発明の臭素除去装置21におい
て陰極26、陽極25共に電極面積100cm2隔膜2
4はイオン交換膜を用い、0.5A、1.8Vで30分間
充電し陰極26上に亜鉛を析出せしめた。
Example 1 In the bromine removal apparatus 21 of the present invention shown in FIG.
No. 4 used an ion exchange membrane and was charged at 0.5 A and 1.8 V for 30 minutes to deposit zinc on the cathode 26.

次に電池運転は陽極液ポンプ11の吐出圧を
0.1Kg/cm2とし陰極液ポンプ12の吐出圧を0.2
Kg/cm2とし、充放電条件は比較例と同じくし、電
流効率を測定した結果93%の高い効率を得た。即
ち比較例の単に液圧差をつけて得られた結果より
8%の向上を示したことになる。
Next, for battery operation, the discharge pressure of the anolyte pump 11 is
0.1Kg/cm 2 and the discharge pressure of catholyte pump 12 is 0.2
Kg/cm 2 , the charging and discharging conditions were the same as in the comparative example, and as a result of measuring the current efficiency, a high efficiency of 93% was obtained. In other words, this is an 8% improvement over the comparative example obtained by simply adding a hydraulic pressure difference.

実施例 2 第5図に示す本発明の臭素除去装置21におい
て隔膜24の面積100cm2、厚み1.2mmの多孔質膜
(旭化成(株)製FP膜)5枚重ねて組み立て配管し本
装置を用いた。バルブ27と28及び陽極液ポン
プ11の入力電圧を調整し電池内部で陰極室から
陽極室への液移動量をこの臭素除去装置21を通
して陰極液貯槽10に戻る液量を同程度とした。
Example 2 In the bromine removal device 21 of the present invention shown in FIG. 5, five porous membranes (FP membrane manufactured by Asahi Kasei Corporation) with a diaphragm 24 having an area of 100 cm 2 and a thickness of 1.2 mm were assembled and piped to use the device. there was. The input voltages of the valves 27 and 28 and the anolyte pump 11 were adjusted so that the amount of liquid transferred from the cathode chamber to the anode chamber inside the battery and the amount of liquid returned to the catholyte storage tank 10 through the bromine removal device 21 were made to be similar.

ポンプ吐出圧は実施例1と、及び電池の充放電
条件は比較例と同じくし、電池を運転し電流効率
を測定した結果90%が得られた。比較例より5%
の向上を示したことになる。
The pump discharge pressure was the same as in Example 1, and the charging and discharging conditions of the battery were the same as in the comparative example, and the battery was operated and the current efficiency was measured, and as a result, 90% was obtained. 5% compared to comparative example
This shows an improvement in

実施例 3 第7図に示す本発明の装置を用い、添加剤とし
て4級アミンの1種であるメチル、デシル、ピロ
リジウム塩 を用い臭素除去装置の容量は300ml、添加剤は前
記の薬剤500g添加し過飽和状態とした。
Example 3 Using the apparatus of the present invention shown in Figure 7, methyl, decyl, and pyrrolidium salts, which are one type of quaternary amine, were added as additives The capacity of the bromine removal device was 300 ml, and 500 g of the above-mentioned additives were added to achieve a supersaturated state.

電池の運転条件は比較例とポンプ吐出圧は実施
例1と同じ条件で運転を行なつた結果電流効率90
%を得た。
The battery was operated under the same conditions as the comparative example and the pump discharge pressure was the same as in Example 1. As a result, the current efficiency was 90.
I got %.

本結果は、比較例より5%の向上を示したこと
による。
This result shows an improvement of 5% over the comparative example.

以上の実施例の結果より明らかな如く、本発明
による亜鉛−臭素電池は電流効率を高率に維持し
うる有用な発明であることは明らかである。
As is clear from the results of the above examples, it is clear that the zinc-bromine battery according to the present invention is a useful invention that can maintain a high current efficiency.

【図面の簡単な説明】[Brief explanation of drawings]

第1図は電解液循環型の亜鉛−臭素二次電池の
基本的構成を示す模式図、第2図は電解液循環型
の亜鉛−臭素二次電池の変形模式図、第3図は実
施例における臭素除去装置の模式図第4図は第3
図の臭素除去装置を備えた本発明の一実施例を示
す亜鉛−臭素二次電池の基本的構成を示す模式図
第5図は同上、他の実施例の臭素除去装置を備え
た亜鉛−臭素二次電池の基本的構成を示す模式
図、第6図は第5図に示す態様と異なる臭素除去
装置の模式図、第7図は同上さらに他の実施例を
示すので臭素を錯化物として除去する臭素除去装
置を備えた亜鉛−臭素二次電池の基本的構成を示
す模式図、第8図は第7図に示す臭素除去装置の
他の実施態様図である。 1:亜鉛臭素電池、2:陽極室、3:陰極室、
4:隔膜、5:陽極、6:陰極、9:陽極液貯
槽、10:陰極液貯槽、11,12:ポンプ、1
8:共通バルブ、19:充放電器、21:臭素除
去装置、25:臭素除去装置用陽極、26:臭素
除去装置用陰極、27,28:バルブ、31,3
2:液室、39:補助電源装置、40:添加剤溶
液。
Figure 1 is a schematic diagram showing the basic configuration of an electrolyte circulation type zinc-bromine secondary battery, Figure 2 is a modified schematic diagram of an electrolyte circulation type zinc-bromine secondary battery, and Figure 3 is an example. Figure 4 is a schematic diagram of the bromine removal equipment in Figure 3.
FIG. 5 is a schematic diagram showing the basic structure of a zinc-bromine secondary battery according to an embodiment of the present invention, which is equipped with the bromine removal device shown in the figure. A schematic diagram showing the basic configuration of a secondary battery, FIG. 6 is a schematic diagram of a bromine removal device different from the embodiment shown in FIG. FIG. 8 is a schematic diagram showing the basic configuration of a zinc-bromine secondary battery equipped with a bromine removing device, and FIG. 8 is a diagram showing another embodiment of the bromine removing device shown in FIG. 1: Zinc bromine battery, 2: Anode chamber, 3: Cathode chamber,
4: diaphragm, 5: anode, 6: cathode, 9: anolyte storage tank, 10: catholyte storage tank, 11, 12: pump, 1
8: common valve, 19: charger/discharger, 21: bromine removal device, 25: anode for bromine removal device, 26: cathode for bromine removal device, 27, 28: bulb, 31, 3
2: Liquid chamber, 39: Auxiliary power supply device, 40: Additive solution.

Claims (1)

【特許請求の範囲】 1 陽極室と陰極室とを隔膜により分離し、陽極
室内の陽極液および陰極室内の陰極液を夫々陽極
液貯槽および陰極液貯槽を経由し循環せしめ、陰
極室内の陰極液圧を陽極室内の陽極液圧より大に
し、陰極液を前記隔膜を通して陽極室内に移動せ
しめるように構成した亜鉛−臭素電池において、
前記陽極液貯槽9と前記陰極液貯槽10間に臭素
除去装置21を設け、該臭素除去装置を介して前
記陽極室内に移動した電解液を陰極液貯槽に戻す
ことを特徴とする亜鉛臭素電池。 2 前記隔膜が多孔質膜であることを特徴とする
特許請求の範囲第1項記載の亜鉛臭素電池。 3 陽極および陰極を備え、陽極室と陰極室は隔
膜により分離された亜鉛臭素電解槽を形成したこ
とよりなる臭素除去装置であり、該臭素除去装置
の陰極室は陽極液貯槽ならびに陰極液貯槽と、陽
極室は陽極液貯槽とを導管により連通してなるこ
とを特徴とする特許請求の範囲第1項記載の亜鉛
臭素電池。 4 臭素除去装置と電池構成部を積層してなるこ
とを特徴とする特許請求の範囲第3項記載の亜鉛
臭素電池。 5 多孔質膜、イオン交換性を賦与した多孔質膜
或はイオン交換膜よりなる隔膜にて分離された複
数の液室よりなる臭素除去装置であり、該臭素除
去装置の前記液室の一端には陽極液貯槽からの陽
極液を導入する導管および調節バルブならびに陽
極液貯槽と連通する導管および調節バルブを備
え、かつ液室の他端と陰極液貯槽は導管により連
通してなることを特徴とする特許請求の範囲第1
項記載の亜鉛臭素電池。 6 臭素除去装置の液室と陽極液貯槽とを導管に
より連通せしめるに当り、該導管の断面積より小
なる導管により前記液室と接続することを特徴と
する特許請求の範囲第5項記載の亜鉛臭素電池。 7 電解液中の臭素を臭素錯化物とせしめる3級
および4級アミン化合物等の添加剤の溶液を封入
したことよりなる臭素除去装置であり、該臭素除
去装置の前記溶液中に陽極液貯槽の陽極液を導入
する導管ならびに陽極液貯槽と連通する導管なら
びに連通導管中に隔膜を備えかつ臭素除去装置の
上部に陰極液貯槽と連通してなることを特徴とす
る特許請求の範囲第1項記載の亜鉛臭素電池。 8 臭素を臭素錯化物とせしめる添加剤が過飽和
であることを特徴とする特許請求の範囲第7項記
載の亜鉛臭素電池。
[Scope of Claims] 1. The anode chamber and the cathode chamber are separated by a diaphragm, and the anolyte in the anode chamber and the catholyte in the cathode chamber are circulated through an anolyte storage tank and a catholyte storage tank, respectively, and the catholyte in the cathode chamber is circulated through an anolyte storage tank and a catholyte storage tank, respectively. In a zinc-bromine battery, the pressure is greater than the anolyte pressure in the anode chamber, and the catholyte is moved through the diaphragm into the anode chamber,
A zinc bromine battery characterized in that a bromine removal device 21 is provided between the anolyte storage tank 9 and the catholyte storage tank 10, and the electrolyte that has moved into the anode chamber is returned to the catholyte storage tank via the bromine removal device. 2. The zinc bromine battery according to claim 1, wherein the diaphragm is a porous membrane. 3 A bromine removal device comprising a zinc-bromine electrolytic cell comprising an anode and a cathode, with the anode chamber and cathode chamber separated by a diaphragm, and the cathode chamber of the bromine removal device is separated from an anolyte storage tank and a catholyte storage tank. 2. The zinc bromine battery according to claim 1, wherein the anode chamber is connected to the anolyte storage tank through a conduit. 4. The zinc bromine battery according to claim 3, characterized in that the bromine removal device and the battery components are stacked. 5 A bromine removal device consisting of a plurality of liquid chambers separated by a porous membrane, a porous membrane imparted with ion exchange properties, or a diaphragm made of an ion exchange membrane, wherein one end of the liquid chamber of the bromine removal device is characterized by comprising a conduit and a control valve for introducing the anolyte from the anolyte storage tank, and a conduit and a control valve that communicate with the anolyte storage tank, and the other end of the liquid chamber and the catholyte storage tank are connected by the conduit. Claim 1
Zinc bromine battery as described in section. 6. The liquid chamber of the bromine removal device and the anolyte storage tank are connected to each other by a conduit having a cross-sectional area smaller than that of the conduit. Zinc bromine battery. 7 A bromine removal device which includes a solution of additives such as tertiary and quaternary amine compounds that convert bromine in an electrolytic solution into a bromine complex, and an anolyte storage tank is placed in the solution of the bromine removal device. Claim 1, characterized in that a conduit for introducing the anolyte, a conduit communicating with the anolyte storage tank, and a diaphragm in the communication conduit, and communicating with the catholyte storage tank in the upper part of the bromine removal device. zinc bromine battery. 8. The zinc-bromine battery according to claim 7, wherein the additive that causes bromine to form a bromine complex is supersaturated.
JP57219165A 1982-12-16 1982-12-16 Zinc-bromine battery Granted JPS59111279A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP57219165A JPS59111279A (en) 1982-12-16 1982-12-16 Zinc-bromine battery

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP57219165A JPS59111279A (en) 1982-12-16 1982-12-16 Zinc-bromine battery

Publications (2)

Publication Number Publication Date
JPS59111279A JPS59111279A (en) 1984-06-27
JPH0367309B2 true JPH0367309B2 (en) 1991-10-22

Family

ID=16731216

Family Applications (1)

Application Number Title Priority Date Filing Date
JP57219165A Granted JPS59111279A (en) 1982-12-16 1982-12-16 Zinc-bromine battery

Country Status (1)

Country Link
JP (1) JPS59111279A (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS61156643A (en) * 1984-12-27 1986-07-16 Toyota Motor Corp Zinc-bromine battery

Also Published As

Publication number Publication date
JPS59111279A (en) 1984-06-27

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